Irrigation Department, CEBAS-CSIC, Campus Universitario de Espinardo, Murcia, P.O. Box 164, E-30100, Spain.
Department of Agricultural Engineering, UPCT, 30203, Cartagena, Spain.
Plant Physiol Biochem. 2021 Jan;158:125-135. doi: 10.1016/j.plaphy.2020.11.048. Epub 2020 Dec 3.
Organic residues (compost) can be used as growth medium but may contain phytotoxic ions that, combined with a water deficit may alter the behavior of plants. The experiment was carried out in a growth chamber with Cistus albidus in a commercial substrate, C (sphagnum peat, coconut fiber and perlite, 8:7:1) and a mixture of compost substrates, Cp (slurry compost, coconut fiber and perlite, 3:6:1). Plants were grown in pots under well-watered, maintaining values of Ψ around -0.9 MPa (WW) and water-stressed (WS) conditions, where the irrigation was removed until reached values of Ψ around -3.0 MPa (water stress period), after then, water was re-established in all plants (recovery period). Although, the well-watered plants had a leaf water potential (Ψ) around -0.9 MPa, stomatal conductance (g) was 125 mmol ms in the commercial substrate and 30 mmol ms-1 in compost. The time taken to reach the threshold value at which water stress occurs was 13 days in the commercial substrate and 53 days in compost. Water-stressed plants in the commercial substrate had significantly lower values of Ψ and g than well-watered. Plants in compost maintained values of g similar in both irrigation treatments (WW and WS) and accumulated less biomass than those that grown in commercial. The water stress in compost led an increase in the adaxial epidermis, parenchyma and mesophyll, whereas water stress in commercial the proportions of the different tissues decreased. Higher lipid peroxidation values were found in plants grown in both substrates under water stress. The recovery time of the plants, until manage Ψ values around -0.9 MPa, depended on the type of substrate. The restoration of irrigation in commercial substrate act as a new stress, as reflected in the photochemical mechanisms.
有机残留物(堆肥)可用作生长介质,但可能含有植物毒性离子,与水分亏缺结合可能会改变植物的行为。该实验在生长室中进行,使用商业基质 C(水苔、椰子纤维和珍珠岩,8:7:1)和堆肥基质混合物 Cp(泥浆堆肥、椰子纤维和珍珠岩,3:6:1)培养白花丹。植物在盆栽中生长,在充分浇水条件下,保持 Ψ 值约为-0.9 MPa(WW)和水分胁迫(WS)条件下,当灌溉停止直到 Ψ 值达到约-3.0 MPa 时(水分胁迫期),然后在所有植物中重新浇水(恢复期)。尽管充分浇水的植物叶片水势(Ψ)约为-0.9 MPa,但在商业基质中的气孔导度(g)为 125 mmol ms-1,在堆肥中为 30 mmol ms-1。在商业基质中达到发生水分胁迫的阈值所需的时间为 13 天,在堆肥中为 53 天。在商业基质中,水分胁迫的植物的 Ψ 和 g 值明显低于充分浇水的植物。在堆肥中,无论是充分浇水还是水分胁迫处理,植物的 g 值都保持相似,并且积累的生物量比在商业基质中生长的植物少。在堆肥中,水分胁迫导致叶表皮、薄壁组织和叶肉的增加,而在商业基质中,不同组织的比例减少。在两种基质中,水分胁迫下的植物都发现了更高的脂质过氧化值。植物的恢复时间,直到管理 Ψ 值约为-0.9 MPa,取决于基质的类型。在商业基质中恢复灌溉会导致新的胁迫,这反映在光化学机制中。